DISSERTATION Copy 2

Total Page:16

File Type:pdf, Size:1020Kb

DISSERTATION Copy 2 Impacts%of%semi7natural%grazing%on% vegetation%biodiversity:%A%study%of%Knepp% Castle%Estate’s%re7wilding%project% Charlotte)L)Bottone) Geography)MA)(Hons)) 2016) Word%count:%11,636% !1 Declaration)of)originality)) 'I%hereby%declare%that%this%dissertation%has%been%composed%by%me%and%is%based%on%my%own% work’% Signature:_________________________% !2 Acknowledgements) Firstly,%I%would%like%to%thank%my%dissertation%supervisor,%Eva%Panagiotakopulu,%for%going%above% and%beyond.% I%would%also%like%to%thank%Charlie%Burrell%and%Penny%Green%at%Knepp%for%allowing%me%to%carry% out%this%research%and%answering%any%questions%that%I%had.%% I%am%thankful%for%all%the%help%and%advice%Michael%Sutcliffe%and%my%family%gave%me.% Finally%thanks%to%my%fellow%geographers,%the%friends%I%have%made%here%at%Edinburgh%have% provided%endless%moral%support%and%comradery.% !3 Abstract)) Re7wilding%is%a%revolutionary%approach%to%conservation,%one%that%aims%to%restore%natural% processes%and%keystone%species%to%play%a%more%prominent%role%in%the%landscape.%In%addition,% re7wilding%allows%society%to%reconnect%with%nature.%Knepp%Castles%Estate’s%re7wilding%project%is% a%unique%experiment%which%endeavours%to%re7introduce%large%grazing%herbivores%into%the% landscape%in%the%hope%that%this%will%eventually%enable%natural%processes%to%take%place%and% improve%Sloral%and%faunal%biodiversity.%This%study%aims%to%assess%the%impacts%of%the%semi7 natural%grazing%at%Knepp,%as%well%as%the%ways%in%which%it%has%affected%the%vegetation% biodiversity.%This%was%achieved%by%carrying%out%vegetation%surveys%and%applying%the%data%to% calculate%vegetation%biodiversity.%The%results%from%each%of%Knepp’s%three%experimental%blocks% highlight%that%different%levels%of%human%intervention%were%involved%in%the%construction%of%these% experiments.%The%different%levels%of%intervention%affected%the%species%of%grazer,%intensity%of% grazing%and%land%restoration%strategies,%which%in%turn%had%consequences%for%the%vegetation% biodiversity.%Although%there%are%numerous%factors%which%can%alter%the%dynamics%of%an% ecosystem,%this%study%found%that%high%grazing%intensity%had%the%most%inSluence%on%retarding% vegetation%biodiversity.%As%well%as%this,%a%fallow%period%(before%the%introduction%of%grazers)% proved%favourable%to%the%formation%or%mosaic%habitats,%and%subsequently,%vegetation% biodiversity.%These%Sindings%provide%suggestions%for%the%future%of%Knepp’s%re7wilding% experiments,%namely%that%further%and%more%controlled%experimentation%would%be%beneSicial% towards%Knepp’s%success%and%the%instruction%of%other%similar%re7wilding%schemes.%% !4 1. Introduction 1 1.1 Aim and Objectives 3 1.2 Background 4 2. Methodology 12 2.1 Site Selection 14 2.2 Field methods 17 2.3 Data analysis 19 3.Results 24 3.1 Data 24 4. Data Analysis 33 4.1 Descriptive statistics 33 4.2 Inferential statistics 36 4.3 Biodiversity Indices 39 4.4 Grazing 41 4.5 Correlations 41 5. Discussion 44 5.1 Biodiversity 44 5.2 Vegetation succession 47 5.3 Co-existence 50 5.4 The effects of grazing on vegetation 52 5.5 Stocking levels 56 5.6 Effects other than grazing herbivores 57 5.7 Wider implications 58 5.8 Suggestions for the future 61 6. Conclusion 62 !5 List of Figures Figure1:%p5% Figure%2:%p6% Figure%3:%p6% Figure%4:%p9% Figure%5:%p12% Figure%6:%p13% Figure%7:%p18% Figure%8:%p32% Figure%9:%p33% Figure%10:%p43% Figure%11:%p35% Figure%12:%p37% Figure%13:%p40% Figure%14:%p42% Figure%15:%p46%% Figure%16:%p48% Figure%17:%p50% Figure%18:%p53% Figure%19:%p55% Figure%20:%p59%% List)of)Tables) Table%1:%p14% Table%2:%p15% Table%3:%p17% Table%4:%p24725% Table%5:%p26727% Table%6:%p28729% Table%7:%p30731% Table%8:%p38% Table%9:%p38% Table%10:%p39% Table%11:%p41% Table%12:%p43% !1 1.)Introduction)) %% % Re7wilding%is%the%mass%restoration%of%ecosystems,%which%attempts%to%recover%areas%of% wilderness.%The%term%re7wilding%was%Sirst%used%by%the%conservation%activist%Dave%Foreman%in% the%1990’s,%but%has%since%been%reSined%by%conservation%biologist%Michael%Soulé%(Fraser,%2009).% He%based%re7wilding%on%three%principles,%Sirstly%that%ecosystems%are%maintained%by%‘top7down’% predators,%second%that%these%animals%require%extensive%space,%and%third%that%they%need% connectivity%(Soulé%and%Noss,%1998).%%In%short%hand%these%are%known%as%the%three%C’s:%cores,% corridors%and%carnivores%(Soulé%and%Noss,%1998).%Since%then,%re7wilding%has%become% popularised%by%writers%such%as%British%environmentalist%George%Monbiot,%who%argues%that%re7 wilding%is%quintessentially%based%on%the%earth%being%a%self7regulating%and%complex%set%of% ecosystems%(Monbiot,%2013).%He%explains%the%importance%of%the%discovery%of%trophic% cascading,%and%highlights%the%key%role%large%animals%play%in%many%aspects%of%an%ecosystem.%In% addition,%he%contends%that%removing%these%animals%causes%drastic%changes%to%a%habitat,%both% directly%and%indirectly%(Monbiot,%2013).%This%makes%for%a%powerful%case%to%re7introduce%large% mammals%and%keystone%species%back%into%the%environment,%not%in%order%to%create%a%particular% type%of%habitat,%but%instead,%to%minimise%human%intervention%in%natural%processes.%% % Re7wilding%has%often%been%mistakenly%described%as%an%attempt%to%turn%back%time,%when% in%fact,%it%is%a%way%of%using%the%past%to%inform%the%present%(Lorimer%et%al.,%2015).%Knepp%Castle% Estate%is%an%example%of%such%a%project,%it%is%a%site%which%uses%large%grazing%herbivores%to%restore% natural%processes%(Knepp,%2016).%The%ecologist%Frans%Vera’s%pioneering%work%in%re7wilding%has% informed%the%project%at%Knepp%(Greenway,%2006).%His%wood7pasture%hypothesis%determined% the%primordial%baseline%for%the%state%of%vegetation%in%Europe%(Vera,%200).% !1 % This%study%assesses%how%the%introduction%of%large%grazing%herbivores%has%inSluenced%the% vegetation%biodiversity%at%Knepp%Castle%estates’%re7wilding%project.%This%is%achieved%by% surveying%the%vegetation%across%three%blocks%of%Knepp%which%have%all%undergone%forms%of%re7 wilding%experiments.%This%study%aims%to%Sill%in%gaps%of%knowledge%in%Knepp’s%re7wilding% project,%no%study%has%been%carried%out%assessing%the%impacts%of%grazing%on%vegetation% biodiversity.%The%data%gathered%during%the%survey%period%was%then%analysed,%and%upon% examination,%the%southern%block%proved%to%be%the%most%successful%at%‘re7wilding’.%This%is% because%the%southern%block%has%progressed%further%in%terms%of%vegetation%succession%due%to%an% optimal%grazing%intensity%of%a%variety%of%large%grazing%herbivores.%The%grazing%herbivores%have% created%intermediate%patterns%of%vegetation%disturbances,%generating%a%mosaic%habitat,%and%in% turn%increasing%vegetation%biodiversity.%This%is%ultimately%indicative%of%a%habitat%undergoing% the%process%of%re7wilding.% !2 1.1)Aim)and)Objectives) The%overall%aim%of%this%study%is:% To#determine#the#effect#of#Semi/natural#Grazing#on#the#vegetation#biodiversity#of##Knepp#Castle# Estate’s#Re/wilding#Project.# In%order%to%achieve%the%above%aim,%this%study%has%three%objectives:% • Examine%current%vegetation%biodiversity%across%the%three%blocks%of%Knepp%Castle%Estate.% %% • Assess%the%impact%of%grazing%herbivores%on%vegetation%biodiversity%by%comparing%the%three% blocks%of%Knepp%Castle%Estate.% %% • Evaluate%which%block%is%most%successful%at%achieving%Knepp’s%re7wilding%aims.% !3 1.2)Background) 1.2.1%Re7wilding% % Broadly%deSined,%re7wilding%is%a%form%of%conservation%aimed%at%protecting%and%restoring% ecological%processes%and%areas%of%wilderness%by%reintroducing%keystone%species%and%apex% predators.%The%preservation%of%wilderness%or%‘wild%places’%was%one%of%the%main%motivations%of% conservation%pioneers%like%John%Muir%in%the%19th%century.%However,%re7wilding%is%a%more% modern%take%on%such%ideas.%Re7wilding%encompasses%a%broad%range%of%projects%globally%with% numerous%approaches,%the%reintroduction%of%wolves%to%Yellowstone%park%is%often%seen%as%the% Slagship%example.%Other%forms%of%re7wilding%include%plestoicene%re7wilding%and%the%use%of% megafauna%analogues%or%island%biogeography%with%the%reintroduction%of%giant%tortoises%in%the% Golapogas%(Hanson%et%al.,%2010).%In%Europe%re7wilding%tends%to%focus%on%naturlistic%grazing% through%the%introduction%of%large%herbivores.%This%has%become%popular%due%to%concerns%over% rural%depopulation%and%intensive%farming%(Macdonald%et%al.,%2000).%Arguably,%some%contention% does%exist%when%it%comes%to%deSining%re7wilding,%for%example,%Svenning%(2015)%argues%that%no% part%of%Europe%could%be%deemed%‘natural’%and%untouched%by%humans,%whereas%Scottish%Natural% Heritage%has%deSined%and%protected%19%%of%current%Scotland%under%the%label%‘wild%land% areas’%(Scottish%Natural%Heritage,%2016).%An%obstacle%for%re7wilding%is%the%nescience%that% misconstrues%re7wilding%as%something%far7fetched,%but%the%restoration%of%wild%places%is%not%a% reverie%of%going%back%to%the%Ice%Age%(Macdonell,%2015).%Nevertheless,%although%re7wilding%has% been%applied%to%a%diverse%range%of%concepts%and%practices,%they%all%share%a%common%aim,%to% maintain,%or%improve,%biodiversity,%while%reducing%the%impact%of%human%interventions%through% the%restoration%of%ecological%processes%(Lorimer%et%al.,%2015).% %% Although%a%vast%array%of%literature%assesses%the%contention%of%what%is%considered%‘wild’% and%‘natural’%(Cronon%1995),%this%study%does%not%discuss%the%theories%of%the%social%construction% !4 of%nature.%This%study%will%refer%to%the%term%natural%based%on%the%mid7holocene%landscape% (around%6000%BP).%This%deSinition%is%chosen%in%parallel%with%Frans%Vera,%who%deSines%a%natural% landscape%as%pre7agricultural,%since%it%involved%little%human%intervention.%% 1.2.3%The%role%of%grazers% Figure%1.%The%forest%cycle%of%vegetation%succession%occurring%with%grazing%
Recommended publications
  • Environmental Weeds of Coastal Plains and Heathy Forests Bioregions of Victoria Heading in Band
    Advisory list of environmental weeds of coastal plains and heathy forests bioregions of Victoria Heading in band b Advisory list of environmental weeds of coastal plains and heathy forests bioregions of Victoria Heading in band Advisory list of environmental weeds of coastal plains and heathy forests bioregions of Victoria Contents Introduction 1 Purpose of the list 1 Limitations 1 Relationship to statutory lists 1 Composition of the list and assessment of taxa 2 Categories of environmental weeds 5 Arrangement of the list 5 Column 1: Botanical Name 5 Column 2: Common Name 5 Column 3: Ranking Score 5 Column 4: Listed in the CALP Act 1994 5 Column 5: Victorian Alert Weed 5 Column 6: National Alert Weed 5 Column 7: Weed of National Significance 5 Statistics 5 Further information & feedback 6 Your involvement 6 Links 6 Weed identification texts 6 Citation 6 Acknowledgments 6 Bibliography 6 Census reference 6 Appendix 1 Environmental weeds of coastal plains and heathy forests bioregions of Victoria listed alphabetically within risk categories. 7 Appendix 2 Environmental weeds of coastal plains and heathy forests bioregions of Victoria listed by botanical name. 19 Appendix 3 Environmental weeds of coastal plains and heathy forests bioregions of Victoria listed by common name. 31 Advisory list of environmental weeds of coastal plains and heathy forests bioregions of Victoria i Published by the Victorian Government Department of Sustainability and Environment Melbourne, March2008 © The State of Victoria Department of Sustainability and Environment 2009 This publication is copyright. No part may be reproduced by any process except in accordance with the provisions of the Copyright Act 1968.
    [Show full text]
  • Plant List Spring Summer Autumn Spring Summer Autumn
    Plant list Spring Summer Autumn Spring Summer Autumn Angelica Wild Bitter-vetch Angelica sylvestris x x Lathyrus linifolius x x Arrowgrass Marsh Blinks Triglochin palustre x x Montia fontana x Asphodel Bog Bluebell Narthecium ossifragum x Hyacinthoides non-scripta x x Bedstraw Heath Bracken Galium saxatile x Pteridium aquilinum x x Bedstraw Marsh Bramble Galium palustre x Rubus fruticosus x x Bird’s foot trefoil Common Bristly Oxtongue Lotus corniculatus x Helminthotheca echioides x Bird’s foot trefoil Greater Buckler-fern Broad Lotus pedunculatus x x x Dryopteris dilatata x x Bistort Alpine Buttercup Bulbous Persicaria vivipara x Ranunculus bulbosus Bitter-cress Wavy Buttercup Creeping Cardamine flexuosa x x x Ranunculus repens x x x Spring Summer Autumn Spring Summer Autumn Buttercup Meadow Club-rush Bristle Ranunculus acris x x x Isolepis setacea x x Butterfly-orchid Greater Cock’s Foot Platanthera chlorantha x Dactylis glomerata x Butterwort Common Corn Spurrey Pinguicula vularis x Spergula arvensis x Canary Grass Reed Cornflower Phalaris arundinacea x x Centaurea cyanus x Cat’s Ear Cotton-grass Common Hypochaeris radicata x x Eriophorum angustifolium x x Challock Cotton-grass Hare’s-tail Sinapis arvensis x Eriophorum vaginatum x Chickweed Common Cow Parsley Stellaria media x Anthriscus sylvestris x Cleavers Crested Dog’s Tail Galium aparine x Cynosurus cristatus x x Clover White Cuckooflower Trifolium repens x x Cardamine pratensis x x Clover Red Cudweed Marsh Trifolium pratense x x Gnaphalium uliginosum x x Clover Zigzag Daisy Trifolium
    [Show full text]
  • Butterfly Surveys, Knepp Castle Estate, 2012
    Butterfly Surveys, Knepp Castle Estate, 2012 Transect Survey, Northern & Middle Blocks (with reference to surveys July 2005 – 2011) Introduction Butterflies have been the subject of annual surveys, usually in July, for a total of eight years (2005-12 inclusive), as part of the overall monitoring programme to assess the effects of the naturalistic grazing regime first implemented in 2001 and since expanded over much of the Knepp Castle Estate. These surveys of the Northern and Middle Blocks were initially conducted by Rich Howarth of the Sussex Wildlife Trust, but in 2012 the task of monitoring butterflies over the wider Wildland project area was taken on by Neil Hulme, Conservation Adviser for the Sussex Branch of Butterfly Conservation. The methodology previously employed by Richworth has been maintained for the Northern and Middle Blocks; namely the standard UKBMS Transect technique, the details of which have been described in earlier reports. The key feature to note is the subdivision of the Transect route into 26 recording ‘parcels’. This year the Transect was walked over two days, as the additional time spent ensuring replication of the exact route precluded completion within an acceptable timeframe. It was also walked later in the year than ideal (10th and 12th August), due to the backlog of other survey work resulting from such poor summer weather. However, the cool, wet summer actually set the butterfly calendar back by two weeks relative to the 21st Century average, so results are remarkably consistent with 2005 – 2011 data. A single July date will be reinstated in 2013. The precise route of previous walks could not be followed in three places, due to both logistical and environmental factors.
    [Show full text]
  • Literature Cited Robert W. Kiger, Editor This Is a Consolidated List Of
    RWKiger 26 Jul 18 Literature Cited Robert W. Kiger, Editor This is a consolidated list of all works cited in volumes 24 and 25. In citations of articles, the titles of serials are rendered in the forms recommended in G. D. R. Bridson and E. R. Smith (1991). When those forms are abbreviated, as most are, cross references to the corresponding full serial titles are interpolated here alphabetically by abbreviated form. Two or more works published in the same year by the same author or group of coauthors will be distinguished uniquely and consistently throughout all volumes of Flora of North America by lower-case letters (b, c, d, ...) suffixed to the date for the second and subsequent works in the set. The suffixes are assigned in order of editorial encounter and do not reflect chronological sequence of publication. The first work by any particular author or group from any given year carries the implicit date suffix "a"; thus, the sequence of explicit suffixes begins with "b". Works missing from any suffixed sequence here are ones cited elsewhere in the Flora that are not pertinent in these volumes. Aares, E., M. Nurminiemi, and C. Brochmann. 2000. Incongruent phylogeographies in spite of similar morphology, ecology, and distribution: Phippsia algida and P. concinna (Poaceae) in the North Atlantic region. Pl. Syst. Evol. 220: 241–261. Abh. Senckenberg. Naturf. Ges. = Abhandlungen herausgegeben von der Senckenbergischen naturforschenden Gesellschaft. Acta Biol. Cracov., Ser. Bot. = Acta Biologica Cracoviensia. Series Botanica. Acta Horti Bot. Prag. = Acta Horti Botanici Pragensis. Acta Phytotax. Geobot. = Acta Phytotaxonomica et Geobotanica. [Shokubutsu Bunrui Chiri.] Acta Phytotax.
    [Show full text]
  • INVASIVE SPECIES Grass Family (Poaceae) Wild Oats Are Annuals
    A PROJECT OF THE SONOMA-MARIN COASTAL PRAIRIE WORKING GROUP INVASIVE SPECIES I NVASIVE A NNUAL P LANTS WILD OATS (AVENA FATUA) AND SLENDER WILD OATS (AVENA BARBATA) - NON-NATIVE Grass Family (Poaceae) Wild oats are annuals. WILD OATS: Are native to Eurasia and North Africa. WILD OAT ECOLOGY Is often dominant or co-dominant in coastal prairie (Ford and Hayes 2007; Sawyer, et al. 2009), Occurs in moist lowland prairies, drier upland prairies and open woodlands (Darris and Gonzalves 2008), Species Interactions: The success of Avena lies in its superior competitive ability: o It has a dense root system. The total root length of a single Avena plant can be from 54.3 miles long (Pavlychenko 1937) to, most likely, twice that long (Dittmer 1937). Wild oats (Avena) in Marin coastal grassland. o It produces allelopathic compounds, Photo by D. (Immel) Jeffery, 2010. chemicals that inhibit the growth of other adjacent plant species. o It has long-lived seeds that can survive for as long as 10 years in the soil (Whitson 2002). Citation: Jeffery (Immel), D., C. Luke, K. Kraft. Last modified February 2020. California’s Coastal Prairie. A project of the Sonoma Marin Coastal Grasslands Working Group, California. Website: www.cnga.org/prairie. Coastal Prairie Described > Species: Invasives: Page 1 of 18 o Pavlychenko (1937) found that, although Avena is a superior competitor when established, it is relatively slow (as compared to cultivated cereal crops wheat, rye and barley) to develop seminal roots in the early growth stages. MORE FUN FACTS ABOUT WILD OATS Avena is Latin for “oat.” The cultivated oat (Avena sativa), also naturalized in California) is thought to be derived from wild oats (Avena fatua) by early humans (Baum and Smith [2011]).
    [Show full text]
  • Eastwood Farm Local Nature Reserve Ecological Survey and Management
    Wessex Ecological Consultancy 28 Egerton Road Bishopston Bristol BS7 8HL EASTWOOD FARM LOCAL NATURE RESERVE ECOLOGICAL SURVEY AND MANAGEMENT RECOMMENDATIONS NOVEMBER 2014 EASTWOOD FARM LOCAL NATURE RESERVE ECOLOGICAL SURVEY AND MANAGEMENT RECOMMENDATIONS INTRODUCTION A series of ecological surveys of Eastwood Farm Local Nature Reserve (LNR) was carried out in autumn 2014, with the intention of informing future management of the site. The aim was to identify habitats and other features of particular ecological value and in particular to highlight those with specific management needs. The survey was carried out late in the year and cannot therefore be regarded as complete: woodland ground flora in particular will have been under recorded. However, sufficient information has been gathered from this survey and existing knowledge of the site to enable a reasonable assessment to be made. SITE DESCRIPTION Eastwood Farm is a diverse site, with examples of several different habitats in a relatively small area; some of these are of nature conservation value in a city-wide context. The descriptions and management recommendations below divide the site into four habitat categories as follows: unimproved and semi-improved grasslands; flood plain and wetland; ancient woodland; and other habitats (secondary woodland and scrub, and amenity grassland). The various areas described below are marked on the attached map. 1 Unimproved and Semi-improved Grasslands 1.1 The most diverse area of grassland on the site is a small field to the south- east of Beese’s Tea Gardens. Frequent grass species here include crested dogstail (Cynosurus cristatus), red fescue (Festuca rubra) and common bent (Agrostis capillaris).
    [Show full text]
  • APPENDIX 1 LANDUSE/HABITAT CLASSIFICATION CODES a Arable
    APPENDIX 1 LANDUSE/HABITAT CLASSIFICATION CODES A Arable AG Unimproved Acid Grassland ALL Allotments AM Amenity Grassland BG Bare Ground BP Broadleaved Parkland BW Broadleaved Woodland CHU Churchyard or Cemetery CS Caravan Site DGM Dry acid grassland/heath mosaic DH Dry Heath DS Dense Scrub DSm Dense Saltmarsh GL Green Lane HOR Horticulture I Improved Grassland IS Introduced Shrubs (ornamental planting) L Lake MG Marshy Grassland NG Unimproved Neutral Grassland PBW Planted Broadleaved Woodland PBW(OR) Orchard Po Pond RES Reservoir SAG Semi-improved Acid Grassland SD Single-species Dominant Swamp SG Coastal Grassland SI Poor Semi-improved Grassland SNG Semi-improved Neutral Grassland SP Short Perennial vegetation SS Scattered Scrub SSm Scattered Saltmarsh SWB Saline Water Body TR Tall Ruderal TS Tall Swamp (mixed species) WG Waste Ground WH Wet Heath APPENDIX 2 SPECIES INDICATIVE OF ANCIENT WOODLAND IN ESSEX Wood Anemone Anemone nemorosa Woodruff * Galium odoratum Nettle-leaved Bellflower * Campanula trachelium Smooth-stalked Sedge * Carex laevigata Pale Sedge * Carex pallescens Pendulous Sedge Carex pendula Remote Sedge Carex remota Thin-spiked Wood Sedge * Carex strigosa Pignut Conopodium majus Lily of the Valley * Convallaria majalis Climbing Fumitory Corydalis claviculata Midland Hawthorn * Crataegus laevigata Scaly Male Fern Dryopteris pseudomas Broad-leaved Helleborine * Epipactis helleborine Purple Helleborine * Epipactis purpurata Spindle Tree Euonymus europaeus Wood Spurge * Euphorbia amygdaloides Yellow Archangel Galeobdolon
    [Show full text]
  • The Morphology and Physiology of Moorland Bracken (Pteridium Aquilinum (L.) Kuhn) and Their Implications for Its Control
    The morphology and physiology of moorland bracken (Pteridium aquilinum (L.) Kuhn) and their implications for its control. A thesis submitted in part examination for the degree of D.Phil. by Sharon J. Whitehead B.A.. Supervisor - Dr. J. Digby Department of Biology, April, 1993. University of York. 1 "To place it in perspective as succinctly as possible, bracken is one hell of a plant". I.A. Evans (1987). 2 TABLE OF CONTENTS page List of tables and figures 8 Acknowledgements 1 3 1. ABSTRACT 1 4 2. INTRODUCTION 1 5 2.1 The importance of bracken as a upland weed 1 5 2.1.1 Distribution 15 2.1.1a Estimated U.K. bracken cover 1 5 2.1.2 Rates of encroachment 1 6 2.1.3 Bracken on the North York Moors 1 6 2.1.4 Explanations for the encroachment of bracken 1 8 2.1.5 Bracken encroachment and the changing environment 20 2.1.6 Problems associated with the presence of bracken 2 0 2.1.6a Economic losses 2 0 2.1.6b Human health risks 22 2.1.6c Ecological and amenity implications 23 2.2 The taxonomy of bracken 25 2.3 Lifecycle 2 6 2.4 The growth and structure of the plant 2 8 2.4.1 Size and age of a bracken plant 2 8 _ 2.4.2 The fronds 28 2.4.3 The rhizome 3 0 2.4.4 Watt's cycle of change 33 2.4.5 The role of apical dominance in bracken 3 5 2.5 Allelopathic chemical production 3 7 2.6 The effect of the environment on bracken growth 3 8 2.7 Bracken control strategies 4 0 2.7.1 Chemical control 4 1 2.7.1a Early bracken control herbicides 4 1 2.7.1b The role of asulam in bracken control 42 2.7.1c Development of new herbicides for bracken 43 2.7.2 Mechanical control 44 2.7.3 Biological control 45 2.8 Summary 4 7 2.9 Project aims 4 8 2.9.1 The morphology of bracken at the interface with Calluna 4 8 2.9.2 Resource acquisition by the margin 4 8 2.9.3-Control of rhizome bud dormancy 4 9 3.
    [Show full text]
  • E5.3 Pteridium Aquilinum Stand
    European Red List of Habitats - Grasslands Habitat Group E5.3 Pteridium aquilinum stand Summary Pteridium aquilinum is naturally a forest fern held in check by the shade of shrubs and trees but, without this cover, and lacking the traditional management of cutting and trampling by cattle, it readily establishes itself as dominant in these bracken stands, overwhelming other vegetation. Spreading vigorously by rhizome extension, the dense shade of the fronds and thick accumulating litter inhibit associated floras, a feature now of many pastoral landscapes less traditionally managed than before. As a consequence of these features, the habitat type is not considered to be of high conservation value. On the contrary, especially in the Atlantic and Subatlantic region of Europe, it can be a threat to other habitats and is sometimes actively controlled by chemical spraying. Synthesis This habitat type is not endangered in either EU28 or EU28+. Overall Category & Criteria EU 28 EU 28+ Red List Category Red List Criteria Red List Category Red List Criteria Least Concern - Least Concern - Sub-habitat types that may require further examination No sub-habitats have been distinguished for further analysis. Habitat Type Code and name E5.3 Pteridium aquilinum stand Bracken field in Ireland, where this Red List type is widely distributed (Photo: Bas In the Scottish highlands, like here on the Isle of Mull, dense stands of Pteridium van Gennip). aquilinum may dominate the hillsides (Photo: Joop Schaminée). Habitat description In the humid regions of Europe bracken (Pteridium aquilinum) may form species-poor 1 to 2 meter high stands on deeper, acidic to neutral, well drained, well aerated and poor to relatively fertile soils.
    [Show full text]
  • <I>Ustilago</I> Species Causing Leaf-Stripe Smut Revisited
    doi:10.5598/imafungus.2018.09.01.05 IMA FUNGUS · 9(1): 49–73 (2018) Ustilago species causing leaf-stripe smut revisited ARTICLE Julia Kruse1,2, Wolfgang Dietrich3, Horst Zimmermann4, Friedemann Klenke5, Udo Richter6, Heidrun Richter6, and Marco Thines1,2,4 1Goethe University Frankfurt am Main, Faculty of Biosciences, Institute of Ecology, Evolution and Diversity, Max-von-Laue-Str. 9, D-60438 Frankfurt am Main, Germany; corresponding authors e-mail: [email protected], [email protected] 2Biodiversity and Climate Research Centre (BiK-F), Senckenberg Gesellschaft für Naturforschung, Senckenberganlage 25, D-60325 Frankfurt am Main, Germany 3Barbara-Uthmann-Ring 68, 09456 Annaberg-Buchholz, Germany 4Cluster for Integrative Fungal Research (IPF), Georg-Voigt-Str. 14-16, D-60325 Frankfurt am Main, Germany 5Grillenburger Str. 8 c, 09627 Naundorf, Germany 6Traubenweg 8, 06632 Freyburg / Unstrut, Germany Abstract: Leaf-stripe smuts on grasses are a highly polyphyletic group within Ustilaginomycotina, Key words: occurring in three genera, Tilletia, Urocystis, and Ustilago. Currently more than 12 Ustilago species DNA-based taxonomy inciting stripe smuts are recognised. The majority belong to the Ustilago striiformis-complex, with about host specificity 30 different taxa described from 165 different plant species. This study aims to assess whether host molecular species discrimination distinct-lineages can be observed amongst the Ustilago leaf-stripe smuts using nine different loci on a multigene phylogeny representative set. Phylogenetic reconstructions supported the monophyly of the Ustilago striiformis- new taxa complex that causes leaf-stripe and the polyphyly of other leaf-stripe smuts within Ustilago. Furthermore, species complex smut specimens from the same host genus generally clustered together in well-supported clades that Ustilaginaceae often had available species names for these lineages.
    [Show full text]
  • The Essex Field Club
    THE ESSEX FIELD CLUB HEADQUARTERS: THE PASSMORE EDWARDS MUSEUM, ROMFORD ROAD, STRATFORD, LONDON, E15 4LZ NEWSLETTER NO. 15 November 1995 FOCUS ON FRESHWATER ALGAE "There are a sort of men whose visages "Do cream and mantle like a standing pond" -The Merchant of Venice, act 1, scene 1, lines 88-89 Some ponds can indeed produce a mantle of green scum, or their water may be entirely green. It is also noticeable how green many trees and fences are in damp weather, as may also be concrete or tarmac paths, tiles, flower pots etc. These manifestations are due to members of the very large and heterogeneous group of the freshwater algae. Yet, apart from the decorative desmids and the intricately patterned diatoms, they have had comparatively few enthusiasts in this country, and as a consequence the occurrence and distribution of the British species is very poorly known. There is no mapping scheme, nor are there more than a few county lists. The plate gives a slight idea of the diversity of algae which are to be found in local ponds and rivers. Most of them are clearly visible with a school-type microscope. There are very many more genera than those illustrated, and some of those genera have dozens or even hundreds of species, many of which are badly described. There is plenty of work for an interested amateur, but one of the chief drawbacks is the need for numbers of large and expensive German monographs when dealing with the smaller species. As the Field Club's recorder for freshwater algae I am prepared to look at any samples members care to send me.
    [Show full text]
  • Holcus Mollis L
    Método de Evaluación Rápida de Invasividad (MERI) para especies exóticas en México Holcus mollis L. CONABIO, 2016 Holcus mollis L. Foto: Lindsey, K.J. 2004. Fuente: Wikipedia. Puede ser introducida como pasto ornamental, por su atractivo follaje rayado (Sagers, 2012). Se considera como una mala hierba en Argentina, América del Norte, Australia, Nueva Zelanda, Sudáfrica y el Reino Unido. H. mollis excluye a otras especies vegetales debido a sus rizomas densamente compactados y porque forma grandes parches clonales que alcanzan 100 m de ancho (VRO, 2016). Información taxonómica Reino: Plantae Phylum: Magnoliophyta Clase: Liliopsida Orden: Poales Familia: Poaceae Género: Holcus Especie: Holcus mollis L. Nombre común: Creeping for grass Resultado: 0.271875 Categoría de riesgo: Alto 1 Método de Evaluación Rápida de Invasividad (MERI) para especies exóticas en México Holcus mollis L. CONABIO, 2016 Descripción de la especie Planta perenne, de tamaño mediano, con rizoma rastrero y delgado. Tallos erectos de 20 - 80 cm de altura, es de color verde grisáceo. Los nodos densamente peludos, más pelos que la vaina. Lígula larga (hasta 5 mm), oval-oblonga. No hay aurícula (Peeters, 2016). Distribución original Nativa de Europa (VRO, 2016). Estatus: Exótica no presente en México ¿Existen las condiciones climáticas adecuadas para que la especie se establezca en México? Sí. 1. Reporte de invasora Especie exótica invasora : Es aquella especie o población que no es nativa, que se encuentra fuera de su ámbito de distribución natural, que es capaz de sobrevivir, reproducirse y establecerse en hábitats y ecosistemas naturales y que amenaza la diversidad biológica nativa, la economía o la salud pública (LGVS).
    [Show full text]